US10626331B2 - Biomass fuel production plant - Google Patents

Biomass fuel production plant Download PDF

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US10626331B2
US10626331B2 US16/077,914 US201716077914A US10626331B2 US 10626331 B2 US10626331 B2 US 10626331B2 US 201716077914 A US201716077914 A US 201716077914A US 10626331 B2 US10626331 B2 US 10626331B2
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heat
carbonized product
lhv
heat medium
drying
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US20190048267A1 (en
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Yuki Endo
Tomoki ICHINOSE
Keiichi Ishikawa
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Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
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Mitsubishi Heavy Industries Environmental and Chemical Engineering Co Ltd
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Assigned to MITSUBISHI HEAVY INDUSTRIES ENVIRONMENTAL & CHEMICAL ENGINEERING CO., LTD. reassignment MITSUBISHI HEAVY INDUSTRIES ENVIRONMENTAL & CHEMICAL ENGINEERING CO., LTD. ASSIGNMENT OF ASSIGNORS INTEREST (SEE DOCUMENT FOR DETAILS). Assignors: ENDO, YUKI, ICHINOSE, TOMOKI, ISHIKAWA, KEIICHI
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    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B57/00Other carbonising or coking processes; Features of destructive distillation processes in general
    • C10B57/08Non-mechanical pretreatment of the charge, e.g. desulfurization
    • C10B57/10Drying
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B41/00Safety devices, e.g. signalling or controlling devices for use in the discharge of coke
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B47/00Destructive distillation of solid carbonaceous materials with indirect heating, e.g. by external combustion
    • C10B47/28Other processes
    • C10B47/30Other processes in rotary ovens or retorts
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B53/00Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form
    • C10B53/02Destructive distillation, specially adapted for particular solid raw materials or solid raw materials in special form of cellulose-containing material
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00Solid fuels
    • C10L5/40Solid fuels essentially based on materials of non-mineral origin
    • C10L5/44Solid fuels essentially based on materials of non-mineral origin on vegetable substances
    • C10L5/447Carbonized vegetable substances, e.g. charcoal, or produced by hydrothermal carbonization of biomass
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10BDESTRUCTIVE DISTILLATION OF CARBONACEOUS MATERIALS FOR PRODUCTION OF GAS, COKE, TAR, OR SIMILAR MATERIALS
    • C10B1/00Retorts
    • C10B1/10Rotary retorts
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2200/00Components of fuel compositions
    • C10L2200/04Organic compounds
    • C10L2200/0461Fractions defined by their origin
    • C10L2200/0469Renewables or materials of biological origin
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/02Combustion or pyrolysis
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/06Heat exchange, direct or indirect
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/08Drying or removing water
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/58Control or regulation of the fuel preparation of upgrading process
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L2290/00Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
    • C10L2290/60Measuring or analysing fractions, components or impurities or process conditions during preparation or upgrading of a fuel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • Y02E50/14
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Definitions

  • the present invention relates to a biomass fuel production plant that performs pyrolysis of wood biomass to produce a carbonized product.
  • carbonizing treatment of the wood biomass is performed in an attempt to improve a heating value.
  • a method of indirectly heating the wood biomass under a low oxygen atmosphere at a high temperature of 300° C. to 700° C. using a pyrolysis furnace such as an external heat type pyrolytic gasification furnace is known. According to this method, a carbonized product with an improved heating value can be produced.
  • high-temperature carbonization in which wood biomass is indirectly heated at a high temperature of 500° C. to 700° C.
  • half carbonization in which wood biomass is indirectly heated at 300° C. or so
  • a carbonized product in which a high gasification rate and spontaneous exothermicity are suppressed can be produced by securing a sufficient treatment time at a predetermined temperature.
  • a carbonized product with both crushability and a residual ratio of heat quantity can be produced by controlling a temperature range to be very narrow see Patent Document 1).
  • the moisture content of the wood biomass that is a raw material for the carbonized product is changed, and thus influences quality of the carbonized product to be produced.
  • control corresponding to the moisture content is required, for instance adjustment of the amount of heating gas supplied to a pyrolysis furnace is performed.
  • the adjustment of the amount of heating gas supplied to the pyrolysis furnace alone is not sufficient, and more stable quality needs to be secured.
  • This invention is directed to further stabilizing quality of a carbonized product to be produced in a, biomass fuel production plant that is configured to perform pyrolysis and carbonization on wood biomass.
  • a biomass fuel production plant includes: a drying heat source configured to generate a heat medium; a drying device configured to use the heat medium supplied from the drying heat source to heat and dry wood biomass; a carbonized product production device configured to perform pyrolysis of the dried wood biomass to produce a carbonized product; a bulk density measurement device configured to measure a bulk density of the carbonized product discharged from the carbonized product production device; and a control device configured to control a heat quantity of the heat medium supplied to the wood biomass in the drying device.
  • the control device includes an LHV calculation unit that is configured to calculate an LHV of the carbonized product from the bulk density. The control device controls the heat quantity of the heat medium supplied to the wood biomass in the drying device on the basis of the calculated LHV.
  • the heat quantity supplied to the wood biomass in the drying device is controlled on the basis of the LHV of the carbonized product which is one index that indicates combustion performance of the carbonized product and which customers may ask to see (LHV is short for “lower heating value,” and refers to a lower heating value or a net heating value)
  • dried biomass having a moisture content that is most suitable for carbonization can be produced. That is, since the heat quantity supplied to the wood biomass is adjusted such that the LHV of the carbonized product becomes a proper value using a correlation between the bulk density and the LHV of the carbonized product, a carbonized product having stable quality can be produced.
  • the drying heat source may includes a combustion furnace that is configured to burn a pyrolytic gas discharged from the carbonized product production device, and a first heat exchanger that is configured to perform heat exchange between a combustion exhaust gas discharged from the combustion furnace and air to generate high-temperature air.
  • the heat medium may be the high-temperature air subjected to heat exchange with the combustion exhaust gas by the first heat exchanger.
  • the combustion furnace is used as the drying heat source, the high-temperature air can be stably generated.
  • the drying heat source may include: a power generation device that uses the high-temperature air as a heat source; and a first waste heat medium line that is configured to supply a waste heat medium having waste heat from the power generation device to the drying device as a heat source.
  • power generation can be performed using heat of the combustion exhaust gas. Waste heat of the power generation can be used as a heat source of the drying device.
  • the drying heat source may include a second heat exchanger that is configured to perform heat exchange between the high-temperature air and a medium for power generation that serves as the heat source of the power generation device.
  • the heat medium may be the high-temperature air that has been subjected to heat exchange with the medium for power generation by the second heat exchanger.
  • the drying heat source may include a second waste heat medium line that is configured to supply the waste heat medium that has been used by the drying device to the power generation device, and a third heat exchanger that is provided on at least one of the first waste heat medium line and the second waste heat medium line, and performs heat exchange between the high-temperature air that has been subjected to heat exchange with the medium for power generation by the second heat exchanger and the waste heat medium.
  • the heat medium may be the high-temperature air that has been subjected to heat exchange with the waste heat medium by the third heat exchanger.
  • the power generation device may be an ORC power generation device that is configured to evaporate a macromolecular organic working medium to perform power generation.
  • the waste heat medium may be hot water that is used to cool the ORC power generation device.
  • the heat quantity supplied to the wood biomass in the drying device is controlled on the basis of the LHV of the carbonized product, dried biomass having a moisture content that is most suitable for carbonization can be produced. That is, because the heat quantity supplied to the wood biomass is adjusted such that the LHV of the carbonized product becomes a proper value using a correlation between the bulk density and the LHV of the carbonized product, a carbonized product having stable quality can be produced.
  • FIG. 1 is a system diagram of a biomass fuel production plant of a first embodiment of the present invention.
  • FIG. 2 is a schematic configurational diagram of a carbonized product production device of the first embodiment of the present invention.
  • FIG. 3 is a graph showing a correlation between an LHV of a carbonized product and a bulk density of the carbonized product.
  • FIG. 4 is a system diagram of a biomass fuel production plant of a second embodiment of the present invention.
  • FIG. 5 is a system diagram of a biomass fuel production plant of a third embodiment of the present invention.
  • FIG. 6 is a system diagram of a power generation device of the biomass fuel production plant of the third embodiment of the present invention.
  • FIG. 7 is a system diagram of a biomass fuel production plant of a fourth embodiment of the present invention.
  • FIG. 1 is a schematic configurational diagram showing an example of a biomass fuel production plant 1 of the present embodiment.
  • the biomass fuel production plant 1 of the present embodiment includes a wood biomass supply device 2 , a drier (a drying device) 3 that dries wood biomass B 1 supplied from the wood biomass supply device 2 , a carbonized product production device 4 that pyrolizes wood biomass B 2 to produce a carbonized product C, a bulk density measurement device 5 that measures a bulk density of the carbonized product C, a drying heat source 13 that produces a heat medium that is a heat source of the drier 3 , and a control device 8 .
  • a wood biomass supply device 2 a drier (a drying device) 3 that dries wood biomass B 1 supplied from the wood biomass supply device 2
  • a carbonized product production device 4 that pyrolizes wood biomass B 2 to produce a carbonized product C
  • a bulk density measurement device 5 that measures a bulk density of the carbonized product C
  • a drying heat source 13 that produces a heat medium that is a heat source of the drier 3
  • a control device 8 .
  • Wood biomass B is biomass (a biological resource) made of wood, and is leftover materials from a forest such as branches, leaves, etc. generated when trees are lumbered or logged, or wood pellets or wood chips produced from bark or sawdust generated from a sawmill or the like.
  • the carbonized product production device 4 has an external heat type pyrolytic gasification furnace (a pyrolysis furnace) 53 of an indirect heating type (see FIG. 2 ) which indirectly heats the wood biomass B to cause a pyrolysis or gasification reaction. Due to progress of pyrolysis, the wood biomass B is carbonized while generating a pyrolytic gas. The produced carbonized product C is discharged to the bulk density measurement device 5 .
  • a pyrolysis furnace a pyrolysis furnace 53 of an indirect heating type (see FIG. 2 ) which indirectly heats the wood biomass B to cause a pyrolysis or gasification reaction. Due to progress of pyrolysis, the wood biomass B is carbonized while generating a pyrolytic gas. The produced carbonized product C is discharged to the bulk density measurement device 5 .
  • the drier 3 is a device that heats and dries the wood biomass B using a heat medium supplied from the drying heat source 13 .
  • the drier 3 dries the wood biomass B having, for instance, a moisture content of 40% to 60% to, for instance, a moisture content of 10% to 20%.
  • a belt drier 3 for drying wood biomass B placed on a belt by spraying a high-temperature dry gas on the wood biomass B may be adopted.
  • the drier 3 may include a rotary kiln type drier or a disk drier.
  • a heating method of the drier 3 may be either indirect heating or direct heating.
  • the drying heat source 13 is, for instance, an incinerator that incinerates waste, and the heat medium is a high-temperature exhaust gas or high-temperature air subjected to heat exchange.
  • the drying heat source 13 is not limited thereto, and a power plant or the like can also be used. Waste heat of the power plant can also be used as a heat source.
  • the drying heat source 13 and the drier 3 are connected by a heat medium line 26 . That is, a heat medium generated by the drying heat source 13 is introduced into the drier 3 via the heat medium line 26 .
  • a control damper 16 for adjusting a flow rate or a heat quantity of the heat medium supplied to the drier 3 is provided on the heat medium line 26 .
  • the control damper 16 can be controlled by the control device 8 .
  • the carbonized product production device 4 has a screw conveyor 52 that conveys the wood biomass B that is the raw material, an external heat type pyrolytic gasification furnace 53 that carbonizes the wood biomass B charged from the screw conveyor 52 by pyrolizing the wood biomass B, and a chute 54 that discharges the carbonized product C discharged from the external heat type pyrolytic gasification furnace 53 .
  • the external heat type pyrolytic gasification furnace 53 is an indirect heating type pyrolysis furnace that indirectly heats the wood biomass B to cause a pyrolysis or gasification reaction.
  • the external heat type pyrolytic gasification furnace 53 is an external heat type rotary kiln type that has an external cylinder (a muffle) 58 and an internal cylinder (a kiln shell) 59 which is rotated relative to the external cylinder 58 and into which the wood biomass B is charged.
  • the external heat type rotary kiln type is used as the external heat type pyrolytic gasification furnace 53 , but the external heat type pyrolytic gasification furnace 53 is not limited thereto as long as it is a type that indirectly heats the wood biomass B.
  • an external heat type screw conveyor or the like may be used as the external heat type pyrolytic gasification furnace 53 .
  • An upstream side of the internal cylinder 59 is supported to be rotatable about an axis by a movable side support 60 that is movable in an axial direction.
  • a downstream side of the internal cylinder 59 is supported to be rotatable about the axis by a stationary side support 63 .
  • the screw conveyor 52 for charging the wood biomass B is provided on the movable side support 60 that configures an inlet part of the internal cylinder 59 .
  • the chute 54 that discharges the carbonized product C is provided on the stationary side support 63 that configures an outlet part of the internal cylinder 59 .
  • the movable side support 60 has an annular frame 61 that rotatably supports the internal cylinder 59 . Opposite lateral parts of the annular frame 61 are rotatably supported by upper ends of a support member 62 that is rockably raised from an installation surface 68 .
  • a plurality of fins (or a spiral (not shown)) arranged to be inclined with respect to a circumferential direction are provided on an inner wall portion of the internal cylinder 59 , and the internal cylinder 59 is driven and rotated at a predetermined rotation speed (e.g., 1 to 5 rpm) by a driving device 64 , so that the wood biomass B charged from the inlet side (the upstream side) thereof can be transferred to the outlet side (the downstream side) thereof while being heated.
  • the internal cylinder 59 may be supported to be rotatable about an axis that is slightly inclined with respect to the horizon. In this case, the wood biomass B may be transferred to the outlet side by the inclination and the rotation of the internal cylinder 59 .
  • the driving device 64 has a gear 65 that is provided on the internal cylinder 59 , a driving motor 66 , and a pinion gear 67 that is mounted on a rotational shaft of the driving motor 66 and is engaged into the gear 65 .
  • the driving device 64 transmits driving of the driving motor 66 to the gear 65 and rotates the gear 65 , thereby rotating the internal cylinder 59 about the axis.
  • the external cylinder 58 is fixed to an installation region via a support member 62 (not shown) in a state in which the rotation and the axial movement of the internal cylinder 59 are permitted and sealing between the external cylinder 58 and the internal cylinder 59 is secured.
  • the movable side support 60 and the stationary side support 63 of the internal cylinder 59 form an air seal between a rotating portion and a non-rotating portion thereof.
  • An expansion 77 for absorbing displacement of the movable side support 60 in an axial direction is provided at a connection portion between the movable side support 60 and the screw conveyor 52 .
  • a heating gas supply pipe 70 that connects the external cylinder 58 to a heating gas combustion furnace 69 that functions as a heater for supplying a heating gas is connected to one end of the external cylinder 58 .
  • a heating gas outgoing pipe 71 is connected to the other end of the external cylinder 58 .
  • a heating gas amount adjusting damper 72 and an induction fan 73 that function as a heating gas amount adjusting device 57 are provided on the heating gas outgoing pipe 71 .
  • a plurality of inspection windows 74 are provided at an upper portion of the external cylinder 58 apart from each other in an axial direction.
  • Non-contact thermometers 75 for measuring temperatures of the kiln shell are provided on the inspection windows 74 to face an outer circumferential surface of the internal cylinder 59 rotated about the axis. Radiation thermometers may be used as the non-contact thermometers 75 .
  • the control device 8 and the non-contact thermometers 75 are communicably connected, and the temperatures of the kiln shell measured by the non-contact thermometers 75 are configured to be input to the control device 8 .
  • temperatures of the kiln shell are temperatures of internal portions of the internal cylinder 59 which are in direct contact with the wood biomass B, they have a high correlation with a pyrolytic temperature of the wood biomass B, and reflect a heating situation well. For this reason, temperature control is performed on the basis of the temperatures of the kiln shell, and thereby a heating temperature can be stably controlled.
  • the control device 8 adjusts an amount of the heating gas by a degree of opening of the heating gas amount adjusting damper 72 and a rotational frequency of the induction fan 73 such that the temperatures of the kiln shell are maintained within a predetermined temperature range.
  • the rotational frequency of the internal cylinder 59 is increased (a rotation speed is raised), and thereby evaporation of moisture is accelerated. As the evaporation of moisture increases, the temperatures of the kiln shell are lowered.
  • the bulk density measurement device 5 has a duct 38 into which the carbonized product C discharged from the chute 54 is introduced, and two storage tanks 36 in which the carbonized product C is stored via the duct 38 .
  • the duct 38 is divided into two ducts at a downstream side. That is, the duct 38 has an upstream side duct 39 provided at an upstream side, a branch part 40 , and a pair of downstream side ducts 41 provided downstream from the branch part 40 .
  • a switching damper 42 is provided on the branch part 40 .
  • the carbonized product C introduced into the upstream side duct 39 from the chute 54 is introduced into any of the downstream side ducts 41 by the switching damper 42 .
  • the pair of downstream side ducts 41 are disposed to introduce the carbonized product C into a first storage tank 36 a and a second storage tank 36 b .
  • the switching damper 42 is controlled by the control device 8 .
  • a level meter 44 and a weighing scale 45 are provided for each of the storage tanks 36 .
  • the level meter 44 is a sensor capable of detecting that a predetermined volume of carbonized product C is stored in each of the storage tanks 36 .
  • the level meter 44 can transmit a signal to the control device 8 .
  • a sensor using infrared rays or a sensor using a contact type switch may be adopted as the level meter 44 .
  • the weighing scale 45 is a device that can measure the weight of the carbonized product C stored in each of the storage tanks 36 .
  • the weighing scale 45 can transmit the measured weight to the control device 8 .
  • the control device 8 includes an LHV calculation unit 47 that calculates an LHV (a lower heating value or a net heating value) of the carbonized product C, and adjusts a heat quantity of the heat medium supplied from the drying heat source 13 to the drier 3 on the basis of the calculated LHV.
  • LHV a lower heating value or a net heating value
  • the moisture content of the wood biomass B decreases. As the LHV of the carbonized product C decreases, the moisture content of the wood biomass B increases.
  • FIG. 3 is a graph showing a correlation between the LHV of the carbonized product C and the bulk density of the carbonized product C.
  • the horizontal axis indicates the LHV [MJ/kg] of the carbonized product C
  • the vertical axis indicates the bulk density [g/cm 3 ] of the carbonized product C.
  • the carbonized product C has a relationship in which a lower bulk density results in a higher LHV and that a higher bulk density results in a lower LHV.
  • the control device 8 of the present embodiment can refer to a table T (see FIG. 1 ) in which the correlation between the bulk density and the LHV of the carbonized product C which is shown in FIG. 3 is stored. That is, the LHV calculation unit 47 of the control device 8 can calculate the LHV of the carbonized product C on the basis of the bulk density of the carbonized product C.
  • the control device 8 When an LHV corresponding to an optimum moisture content of the wood biomass B is set to X [MJ/kg], the control device 8 reduces a heat quantity supplied to the wood biomass B when the LHV of the carbonized product C is higher than X. The control device 8 increases the heat quantity supplied to the wood biomass B when the LHV is lower than X.
  • the method of producing the carbonized product C of the present embodiment has a wood biomass drying process of drying the wood biomass B, a pyrolyizing process of performing pyrolysis of the wood biomass B to carbonize the wood biomass B, an LHV calculating process of calculating an LHV of a carbonized product C that is the carbonized wood biomass B, and a supplied heat quantity controlling process of controlling a heat quantity supplied to the wood biomass B per unit time in the drying process on the basis of the calculated LHV.
  • the wood biomass B charged into the drier 3 from the wood biomass supply device 2 is dried by the heat medium supplied from the drying heat source 13 .
  • the wood biomass B dried by the drier 3 is introduced into the internal cylinder 59 of the external heat type pyrolytic gasification furnace 53 by the screw conveyor 52 .
  • a heating gas is supplied from the heating gas combustion furnace 69 into the external cylinder 58 of the external heat type pyrolytic gasification furnace 53 by an induction action of the induction fan 73 , and the internal cylinder 59 located inside the external cylinder 58 is heated from an outer circumferential surface thereof by the heating gas.
  • the wood biomass B introduced into the internal cylinder 59 is indirectly heated and carbonized under a low oxygen atmosphere at a high temperature of 300° C. to 700° C.
  • the wood biomass B is heated while being transferred to the outlet side of the internal cylinder 59 along with rotation of the internal cylinder 59 . Thereby, moisture remaining in the wood biomass B is evaporated first. With the completion of the moisture evaporation, pyrolysis of organic components makes progress. With the progress of the pyrolysis, the wood biomass B is carbonized while generating a pyrolytic gas G. The carbonized wood biomass B is discharged from the chute 54 as a produced carbonized product C (solid fuel) having a predetermined degree of carbonization.
  • a produced carbonized product C solid fuel
  • the pyrolytic gas G generated by pyrolysis is introduced from the chute 54 into the heating gas combustion furnace 69 , and is burnt along with auxiliary fuel or combustion air subjected to heat exchange with the heating gas outgoing pipe 71 .
  • a part of the burnt gas flows back to the heating gas combustion furnace 69 , is burned in the heating gas combustion furnace 69 along with the auxiliary fuel, and is used for heating of the external heat type pyrolytic gasification furnace 53 .
  • a heat quantity supplied to the wood biomass B per unit time is adjusted by the control device 8 .
  • the LHV calculating process is a process of an of the produced carbonized product C.
  • the carbonized product C discharged via the chute 54 is introduced into one of the storage tanks 36 (here, the first storage tank 36 a ).
  • the level meter 44 sends a signal to the control device 8 .
  • control device 8 When the control device 8 receives a signal from the level meter 44 , it obtains weight of the carbonized product C from the weighing scale 45 at that point in time.
  • the bulk density of the carbonized product C can be calculated according to the “bulk density testing method” described in section 6 of JIS K 2151.
  • the carbonized product C inside the first storage tank 36 a is discharged by a predetermined method.
  • the control device 8 operates the switching damper 42 such that the level meter 44 of the first storage tank 36 a transmits the signal and, at the same time, the carbonized product C is introduced into the other of the storage tanks 36 (the second storage tank 36 b ). Thereby, the carbonized product C is stored in the second storage tank 36 b .
  • an LHV of the carbonized product C is calculated by the same method as the method of calculating the LHV of the carbonized product C in the first storage tank 36 a.
  • the bulk density of the carbonized product C can be continuously calculated.
  • the LHV calculation unit 47 calculates the LHV of the carbonized product C stored in the storage tanks 36 using the table T in which the correlation between the LHV of the carbonized product C and the bulk density of the carbonized product C (the correlation represented by the graph of FIG. 3 ) is stored.
  • the control device 8 controls the control damper 16 on the basis of the LHV of the carbonized product C which is calculated by the LHV calculation unit 47 .
  • the control device 8 gives an instruction to lower the LHV of the carbonized product C when the LHV of the carbonized product C is higher than X, that is, when the bulk density of the carbonized product C is low. That is, the control device 8 reduces a heat quantity of the heat medium supplied from the heat medium line 26 to the drier 3 by closing the control damper 16 .
  • the control device 8 gives an instruction to increase the LHV of the carbonized product C when the LHV of the carbonized product C is lower than X, that is, when the bulk density of the carbonized product C is high. That is, the control device 8 increases a heat quantity of the heat medium supplied from the heat medium line 26 to the drier 3 by opening the control damper 16 .
  • the heat quantity supplied to the wood biomass B inside the drier 3 per unit time is controlled on the basis of the bulk density of the carbonized product C in order to set the carbonized product C to a predetermined LHV, dried biomass having a moisture content that is most suitable for carbonization can be produced. That is, since the heat quantity supplied to the wood biomass B inside the drier 3 is adjusted such that the LHV of the carbonized product C has a proper value using the correlation between the LHV of the carbonized product C and the bulk density of the carbonized product C, the carbonized product C having stable quality can be produced.
  • the LHV of the carbonized product C is calculated using the correlation between the bulk density of the carbonized product C and the LHV of the carbonized product C, so that the LHV of the carbonized product C can be rapidly grasped. Due to a high correlation between the LHV of the carbonized product C and the bulk density of the carbonized product C, the LHV of the carbonized product C can be immediately calculated, compared to, for instance, a method of analyzing the carbonized product C.
  • the two storage tanks 36 are used for the bulk density measurement device 5 , but the embodiment is not limited thereto.
  • the embodiment may be configured to measure the bulk density using one of the storage tanks 36 as long as the stored carbonized product C can be rapidly discharged.
  • three or more storage tanks 36 may be installed.
  • a biomass fuel production plant 1 B of the present embodiment includes a wood biomass supply device 2 , a drier 3 that dries wood biomass B supplied from the wood biomass supply device 2 , a carbonized product production device 4 that produces a carbonized product C from the wood biomass B, a bulk density measurement device 5 that measures a bulk density of the carbonized product C, a combustion furnace 6 that burns a pyrolytic gas G discharged from the carbonized product production device 4 , an air preheater (a first heat exchanger) 9 that performs heat exchange between a combustion exhaust gas EG discharged from the combustion furnace 6 and air to produce high-temperature air, and a control device 8 .
  • a wood biomass supply device 2 As shown in FIG. 4 , a biomass fuel production plant 1 B of the present embodiment includes a wood biomass supply device 2 , a drier 3 that dries wood biomass B supplied from the wood biomass supply device 2 , a carbonized product production device 4 that produces a carbonized product C from the wood biomass B, a bulk
  • a drying heat source 13 of the drier 3 of the present embodiment includes the combustion furnace 6 and the air preheater 9 .
  • the air preheater 9 and the drier 3 are connected by a heat medium line 26 B.
  • a control damper 16 B for adjusting a flow rate or a heat quantity of high-temperature air supplied to the drier 3 is provided on the heat medium line 26 B.
  • the control damper 16 B can be controlled by the control device 8 .
  • the combustion furnace 6 can be used as, for instance, a facility for incinerating sludge by agitating and mixing the sludge in a high-temperature fluidized bed.
  • the combustion furnace 6 only needs to be an incineration facility that incinerates waste, biomass, or fossil fuel to discharge a high-temperature exhaust gas.
  • An incineration facility such as a bubble type fluidized furnace, a circulation type fluidized furnace, a pulverized coal combustion furnace, or the like can be adopted as the combustion furnace 6 .
  • the combustion exhaust gas EG is discharged from the combustion furnace 6 via a first combustion exhaust gas line 17 and a second combustion exhaust gas line 18 .
  • the temperature of the combustion exhaust gas EG discharged from the combustion furnace 6 is, for instance, 1000° C.
  • the combustion exhaust gas EG introduced into the first combustion exhaust gas line 17 is supplied to the air preheater 9 , and is used to preheat air.
  • the combustion exhaust gas EG introduced into the second combustion exhaust gas line 18 is supplied to the carbonized product production device 4 , and is used to heat the wood biomass B.
  • a pyrolytic gas G generated in connection with the production of the carbonized product C in the carbonized product production device 4 is supplied to the combustion furnace 6 via the pyrolytic gas line 14 .
  • the control device 8 adjusts the flow rate of the high-temperature air supplied to the drier 3 via the heat medium line 26 B on the basis of a calculated LHV.
  • the combustion furnace 6 is used as the drying heat source 13 , the high-temperature air can be stably produced.
  • a biomass fuel production plant 1 C of the present embodiment includes a power generation device 7 that generates electricity using heat medium oil (a medium for power generation) HO as a heat source, an air preheater 9 that performs heat exchange between a combustion exhaust gas EG discharged from a combustion furnace 6 and air A 1 to produce high-temperature air A 2 , and an oil heater (a second heat exchanger) 10 that performs heat exchange between the high-temperature air A 2 discharged from the air preheater 9 and the heat medium oil HO, all of which are used as a drying heat source 13 for a drier 3 .
  • heat medium oil a medium for power generation
  • the air preheater 9 is a heat exchanger that heat-exchanges (preheats) the combustion exhaust gas EG discharged from the combustion furnace 6 and the air A 1 , and supplies the heat-exchanged high-temperature air A 2 to the oil heater 10 .
  • the combustion exhaust gas EG that has been completely used and is discharged from the air preheater 9 is treated by an exhaust gas treatment device 12 .
  • the exhaust gas treatment device 12 may be configured to have, for instance, a dust collector (a bag filter) that performs a dust collection treatment of the combustion exhaust gas EG, a scrubber that brings a cleaning solution into contact with the combustion exhaust gas EG and makes the combustion exhaust gas EG harmless, and a chimney that discharges the treated combustion exhaust gas EG to the atmosphere.
  • a dust collector a bag filter
  • a scrubber that brings a cleaning solution into contact with the combustion exhaust gas EG and makes the combustion exhaust gas EG harmless
  • a chimney that discharges the treated combustion exhaust gas EG to the atmosphere.
  • the oil heater 10 is a heat exchanger that heat-exchanges (heats) the high-temperature air A 2 discharged from the air preheater 9 and the heat medium oil HO supplied to the power generation device 7 .
  • the power generation device 7 adopts a so-called binary waste heat power generation system (an organic Rankine cycle waste heat power generation system or an organic Rankine cycle power generation device (ORC power generation device)) that performs power generation by heating and evaporating a macromolecular organic working medium using waste heat (the combustion exhaust gas EG) of the combustion furnace 6 as a heat source, and rotating a steam turbine with steam.
  • binary waste heat power generation system an organic Rankine cycle waste heat power generation system or an organic Rankine cycle power generation device (ORC power generation device)
  • ORC power generation device organic Rankine cycle power generation device
  • the power generation device 7 performs power generation using heat of the heat medium oil HO heated by the oil heater 10 .
  • the power generation device 7 has an evaporator 30 that heats and evaporates an organic working medium M using heat of the heat medium oil HO supplied to the power generation device 7 , a steam turbine 31 that is rotated by steam of the organic working medium M, a power generator 32 that is directly connected to the steam turbine 31 , and a condenser 33 that cools the organic working medium M guided from the steam turbine 31 .
  • Hot water (e.g., about 90° C., a waste heat medium) discharged from the condenser 33 is introduced into the drier 3 via a first waste heat medium line 49 , and is used as a drying heat source.
  • Hot water (e.g., about 50° C.) used as the drying heat source at the drier 3 is discharged via a second waste heat medium line 50 , and is supplied to the condenser 33 of the power generation device 7 .
  • high-temperature air A 3 subjected to heat exchange with the heat medium oil HO by the oil heater 10 is supplied to the drier 3 via a high-temperature air line 34 .
  • a control damper 16 C for adjusting a flow rate or a heat quantity of the high-temperature air A 3 supplied to the drier 3 is provided on the high-temperature air line 34 .
  • the control damper 16 C can be controlled by a control device 8 . That is, the control device 8 adjusts the flow rate of the high-temperature air A 3 supplied to the drier 3 via the high-temperature air line 34 on the basis of a calculated LHV.
  • power generation can be performed using the heat of the combustion exhaust gas EG.
  • waste heat of the power generation can be used as the heat source of the drier 3 .
  • a biomass fuel production plant 1 D of the present embodiment includes a heat exchanger (a third heat exchanger) 11 provided on a second waste heat medium line 50 .
  • a supply path of high-temperature air A 3 (e.g., about 200°C.) discharged from an oil heater 10 is different.
  • the high-temperature air A 3 discharged from the oil heater 10 branches off into a first high-temperature air line 19 and a combustion air line 15 , and is supplied to them.
  • the high-temperature air A 3 flowing through the combustion air line 15 is supplied to a combustion furnace 6 as combustion air.
  • a first control damper 21 for adjusting the flow rate of the combustion air flowing along the combustion air line 15 is provided on the combustion air line 15 .
  • a first atmosphere discharge line 27 for discharging the high-temperature air A 3 to the atmosphere branches off from a region of the combustion air line 15 which is located upstream from the first control damper 21 .
  • a second control damper 22 for adjusting a flow rate of the high-temperature air is provided on the first atmosphere discharge line 27 .
  • the second control damper 22 is controlled from a “closed” state to an “opened” state, the high-temperature air A 3 is discharged to the atmosphere via a second atmosphere discharge line 28 connected to the first atmosphere discharge line 27 .
  • the high-temperature air A 3 discharged from the oil heater 10 is supplied to the heat exchanger 11 via a first high-temperature air line 19 .
  • the high-temperature air A 3 supplied to the heat exchanger 11 is used to heat hot water discharged from a drier 3 .
  • the hot water is heated to, for instance, about 60° C.
  • the second atmosphere discharge line 28 for discharging the high-temperature air A 3 to the atmosphere branches off from the first high-temperature air line 19 .
  • a third control damper 23 for adjusting a flow rate of the high-temperature air is provided on the second atmosphere discharge line 28 .
  • the third control damper 23 is controlled from a “closed” state to an “opened” state, the high-temperature air A 3 is discharged to the atmosphere via the second atmosphere discharge line 28 .
  • the third control damper 23 is disposed on the second atmosphere discharge line 28 and upstream from a connection point between the first atmosphere discharge line 27 and the second atmosphere discharge line 28 .
  • High-temperature air A 4 (e.g., about 100° C.) discharged from the heat exchanger 11 is supplied to the drier 3 via a second high-temperature air line 20 .
  • a fifth control damper 25 for adjusting a flow rate of the high-temperature air A 4 is provided on the second high-temperature air line 20 .
  • a fourth control damper 24 for adjusting the flow rate of the high-temperature air A 4 is provided on the third atmosphere discharge line 29 .
  • the fourth control damper 24 is controlled from a “closed” state to an “opened” state, the high-temperature air A 4 is discharged to the atmosphere via the second atmosphere discharge line 28 connected to the third atmosphere discharge line 29 .
  • the control device 8 controls the control damper 16 as shown in Table 1 below.
  • the “closed” state means that the control damper fully closes a flow passage.
  • the “opened” state means that the control damper not only opens a flow passage but also opens a flow passage to perform control in a direction in which the control damper further opens the flow passage within the opened range (a direction in which the control damper widens the flow passage) or in a direction in which the control damper closes the flow passage (a direction in which the control damper narrows the flow passage).
  • the first control damper 21 is properly controlled depending on the flow rate of the combustion air required for the combustion furnace 6 .
  • the second control damper 22 , the third control damper 23 , and the fifth control damper 25 are closed at normal times. That is, the high-temperature air is supplied to the heat exchanger 11 , so that the hot water supplied to the power generation device 7 via the second waste heat medium line 50 is heated.
  • the fourth control damper 24 is closed, and the fifth control damper 25 is opened, so that the high-temperature air A 4 that has been used at the heat exchanger 11 is used for the drier 3 as an auxiliary heat source.
  • the fifth control damper 25 When it is determined that the LHV is high and the heat of the drier 3 is excessive, that is, when the moisture content of the wood biomass B is low, the fifth control damper 25 is closed, and the third control damper 23 and the fourth control damper 24 are opened, so that an amount of supply of the high-temperature air supplied to the combustion furnace 6 and an amount of supply of the high-temperature air supplied to the heat exchanger 11 are reduced. That is, a part of the high-temperature air is discharged to the atmosphere.
  • the above embodiment is configured to control the plurality of control dampers to discharge a part of the high-temperature air to the atmosphere, so that it is possible to cope with a greater change in the moisture content.
  • the heat exchanger 11 is provided on the second waste heat medium line 50 .
  • the heat exchanger 11 may be provided on the first waste heat medium line 49 , and heat the hot water supplied to the drier 3 .

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Citations (14)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2973306A (en) * 1957-02-18 1961-02-28 Charles F Stromeyer Process for producing charcoal and apparatus therefor
US4090945A (en) * 1977-03-25 1978-05-23 Paraho Corporation Method of operating an oil shale kiln
JPH0380295U (ja) 1989-12-06 1991-08-16
US5423455A (en) * 1993-06-25 1995-06-13 Acrison, Inc. Materials feeding system with level sensing probe and method for automatic bulk density determination
US5821396A (en) 1997-01-10 1998-10-13 Bouziane; Richard Batch process for recycling hydrocarbon containing used materials
US20080078552A1 (en) * 2006-09-29 2008-04-03 Osum Oil Sands Corp. Method of heating hydrocarbons
JP2008180451A (ja) 2007-01-25 2008-08-07 Mitsubishi Heavy Ind Ltd 外熱式ロータリーキルンおよびその運転方法
US20110214343A1 (en) * 2010-03-08 2011-09-08 Mark Wechsler Device and method for conversion of biomass to biofuel
US20120055775A1 (en) * 2009-05-14 2012-03-08 Chaotech Pty Ltd pyrolytic process and apparatus for producing biomass char and energy
JP2012219176A (ja) 2011-04-08 2012-11-12 Hitachi Ltd バイオマスの半炭化燃料の製造装置と製造方法、及び半炭化燃料を用いた発電システム
US8388813B1 (en) 2012-01-11 2013-03-05 Earth Care Products, Inc. High energy efficiency biomass conversion process
JP2014065807A (ja) 2012-09-25 2014-04-17 Nippon Paper Industries Co Ltd 固体燃料の製造方法及び固体燃料
JP2015010137A (ja) 2013-06-27 2015-01-19 日本製紙株式会社 固体燃料の製造方法及び固体燃料
US20180208851A1 (en) * 2015-07-30 2018-07-26 Mitsubishi Heavy Industries Environmental & Chemical Engineering Co., Ltd. Carbide producing method and carbide producing device

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0380295A (ja) * 1989-08-24 1991-04-05 Ricoh Co Ltd 文字記号画像形成装置
JP2009191085A (ja) * 2008-02-12 2009-08-27 Mhi Environment Engineering Co Ltd 固体燃料製造方法及びシステム、並びに固体燃料
JP2010229259A (ja) * 2009-03-26 2010-10-14 Tokyo Electric Power Co Inc:The 微粉炭ボイラ用のバイオマス燃料の製造方法
JP6066809B2 (ja) * 2013-04-10 2017-01-25 三菱重工環境・化学エンジニアリング株式会社 バイオマス熱分解装置、及び発電システム

Patent Citations (15)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US2973306A (en) * 1957-02-18 1961-02-28 Charles F Stromeyer Process for producing charcoal and apparatus therefor
US4090945A (en) * 1977-03-25 1978-05-23 Paraho Corporation Method of operating an oil shale kiln
JPH0380295U (ja) 1989-12-06 1991-08-16
US5423455A (en) * 1993-06-25 1995-06-13 Acrison, Inc. Materials feeding system with level sensing probe and method for automatic bulk density determination
US5821396A (en) 1997-01-10 1998-10-13 Bouziane; Richard Batch process for recycling hydrocarbon containing used materials
US20080078552A1 (en) * 2006-09-29 2008-04-03 Osum Oil Sands Corp. Method of heating hydrocarbons
JP2008180451A (ja) 2007-01-25 2008-08-07 Mitsubishi Heavy Ind Ltd 外熱式ロータリーキルンおよびその運転方法
US20120055775A1 (en) * 2009-05-14 2012-03-08 Chaotech Pty Ltd pyrolytic process and apparatus for producing biomass char and energy
US20110214343A1 (en) * 2010-03-08 2011-09-08 Mark Wechsler Device and method for conversion of biomass to biofuel
JP2012219176A (ja) 2011-04-08 2012-11-12 Hitachi Ltd バイオマスの半炭化燃料の製造装置と製造方法、及び半炭化燃料を用いた発電システム
US20140026791A1 (en) 2011-04-08 2014-01-30 Hitachi Ltd Device and Method for Manufacturing Semi-Carbonized Fuel of Biomass, and Power Generation System Using Semi-Carbonized Fuel
US8388813B1 (en) 2012-01-11 2013-03-05 Earth Care Products, Inc. High energy efficiency biomass conversion process
JP2014065807A (ja) 2012-09-25 2014-04-17 Nippon Paper Industries Co Ltd 固体燃料の製造方法及び固体燃料
JP2015010137A (ja) 2013-06-27 2015-01-19 日本製紙株式会社 固体燃料の製造方法及び固体燃料
US20180208851A1 (en) * 2015-07-30 2018-07-26 Mitsubishi Heavy Industries Environmental & Chemical Engineering Co., Ltd. Carbide producing method and carbide producing device

Non-Patent Citations (9)

* Cited by examiner, † Cited by third party
Title
Google machine translation of JP 03-080295U (Year: 1991). *
Meyer et al., "Design and Build of a 1 Kilowatt Organic Rankine Cycle Power Generator", 35th New Zealand Geothermal Workshop: 2013 Proceedings, Nov. 17-20, 2013, Rotorua, New Zealand , Available online at: https://www.geothermalenergy.org/pdf/IGAstandard/NZGW/2013/Meyer_Final.pdf (Year: 2013). *
PCT/ISA/210, "International Search Report for International Application No. PCT/JP2015/071643," dated Oct. 13, 2015.
PCT/ISA/210, "International Search Report for International Application No. PCT/JP2017/005500," dated Mar. 14, 2017.
PCT/ISA/237 "Written Opinion of the International Searching Authority for International Application No. PCT/JP2015/071643," dated Oct. 13, 2015.
PCT/ISA/237, "Written Opinion of the International Searching Authority for International Application No. PCT/JP2017/005500," dated Mar. 14, 2017.
Quaak et al., "Energy from Biomass: A Review of Combustion and Gasification Technologies, vols. 23-422" 1999, World Bank Publications, pp. 3 and 4, avialable online at: https://books.google.com/books?id=M2WMrePlIxkC&dq=relationship+between+LHV+and+bulk+density&source=gbs_navlinks_s (Year: 1999). *
U.S.P.T.O., "Final Rejection for U.S. Appl. No. 15/745,909," dated Nov. 25, 2019.
U.S.P.T.O., "Non-Final Rejection for U.S. Appl. No. 15/745,909," dated Aug. 9, 2019.

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